1. 西安热工研究院有限公司
2. 华能聊城热电有限公司
3. 华北电力大学新能源学院
纸质出版:2026
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程广文, 赵新山, 徐明新, 等. 烟气热解回收废旧风电叶片技术研究[J]. 热力发电, 2026,(10).
程广文, 赵新山, 徐明新, et al. 烟气热解回收废旧风电叶片技术研究[J]. Thermal Power Generation, 2026, (10).
程广文, 赵新山, 徐明新, 等. 烟气热解回收废旧风电叶片技术研究[J]. 热力发电, 2026,(10). DOI: 10.19666/j.rlfd.202602007.
程广文, 赵新山, 徐明新, et al. 烟气热解回收废旧风电叶片技术研究[J]. Thermal Power Generation, 2026, (10). DOI: 10.19666/j.rlfd.202602007.
【目的】热解法是废旧风电叶片回收的主流技术,存在能耗高、次生污染大、回收纤维品质差等缺点,限制了其大规模工程应用。为解决上述问题,本文研究了燃煤烟气热解回收废旧风电叶片新技术。【方法】在模拟燃煤烟气工况下,考察了烟气温度、热解时间、烟气组分和加热方式对回收纤维品质的影响,分析了热解机理;同时,搭建中试试验台在真实烟气条件下验证了所开发的回收技术,并制定了工程应用方案。【结果】结果表明:用燃煤烟气直接加热风电叶片,可使叶片的树脂基体先碳化后氧化,得到较为纯净的玻璃纤维,从而实现风电叶片的回收利用。模拟烟气工况下,叶片热解最佳工艺是:烟气温度500~530℃,热解时间4~5 h。烟气中SO
2
对回收纤维品质无显著影响。回收得到的玻璃纤维纯度大于99%,其拉伸强度较原纤维下降小于10%。利用风机分别从电厂锅炉省煤器入口烟道和空气预热器出口烟道抽取不同烟温的烟气混合均匀,再高温除尘后(烟气温度控制在400~500℃)进入特制的热解炉中与叶片直接接触,热解叶片,可回收得到玻璃纤维,同时热解尾气被实时送入电厂锅炉炉膛,使尾气中的焦油和挥发性组分充分燃烧,生成CO
2
、H_2O和少量NO
x
等污染物,借助电厂现有环保装置协同处置后排入大气。热解过程微放热,热解尾气对电厂污染物排放影响甚微。【结论】烟气热解作为新型回收技术,清洁高效、能耗低、工程可实施性强,可有效破解风机退役引发的废旧叶片处置难题。
[Objective
]
Pyrolysis represents a mainstream technology for the recycling of waste wind turbine blades. Nevertheless
it is plagued by several shortcomings
including high energy consumption
severe secondary pollution
and inferior quality of recovered fibers
which have restricted its large-scale engineering application. To tackle the aforementioned issues
a novel technology for recycling waste wind turbine blades via pyrolysis using coal-fired flue gas was investigated in this study. [Methods
]
Under simulated coal-fired flue gas conditions
the influences of flue gas temperature
pyrolysis duration
flue gas composition
and heating mode on the quality of rec
overed fibers were examined
and the corresponding pyrolysis mechanism was analyzed. Meanwhile
a pilot-scale test rig was established to validate the developed recycling technology under real flue gas conditions
and an engineering application scheme was formulated. [Results
]
The results indicate that direct heating of wind turbine blades with coal-fired flue gas can induce sequential carbonization and subsequent oxidation of the resin matrix in the blades
yielding relatively pure glass fibers and thus realizing the recycling of waste wind turbine blades. Under simulated flue gas conditions
the optimal pyrolysis process parameters for the blades are determined as follows: a flue gas temperature of 500-530 ℃ and a pyrolysis time of 4-5 h. SO
2
in the flue gas exerts no significant effect on the quality of recovered fibers. The purity of the recovered glass fibers is higher than 99%
and the reduction in tensile strength is less than 10% compared with virgin fibers. Flue gases at different temperatures are separately extracted from the inlet flue of the economizer and the outlet flue of the air preheater in the power plant boiler by a fan
mixed uniformly
and subjected to high-temperature dust removal(with the flue gas temperature controlled at 400-500 ℃) before entering a specially designed pyrolysis furnace for direct contact with waste blades to accomplish pyrolysis. Glass fibers can be recovered from the pyrolyzed blades
while the pyrolysis tail gas is synchronously fed into the furnace of the power plant boiler to achieve sufficient combustion of tar and volatile components in the tail gas
generating CO
2
H_2O
and a small amount of NO
x
. The treated tail gas is finally discharged after collaborative disposal by the existing environmental protection facilities of the power plant. The pyrolysis process is slightly exothermic
and the pyrolysis tail gas has a negligible impact on the pollutant emission performance of the power plant. [Conclusion
]
As an innovative recycling te
chnology
flue gas pyrolysis features cleanliness
high efficiency
low energy consumption and strong engineering feasibility
which can effectively address the disposal challenges of waste blades caused by decommissioned wind turbines.
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